alexa Diethylaminoethyl Cellulose Immobilized Pointed Gourd (Trichosanthes dioica) Peroxidase in Decolorization of Synthetic Dyes | Open Access Journals
ISSN: 2155-9821
Journal of Bioprocessing & Biotechniques
Like us on:
Make the best use of Scientific Research and information from our 700+ peer reviewed, Open Access Journals that operates with the help of 50,000+ Editorial Board Members and esteemed reviewers and 1000+ Scientific associations in Medical, Clinical, Pharmaceutical, Engineering, Technology and Management Fields.
Meet Inspiring Speakers and Experts at our 3000+ Global Conferenceseries Events with over 600+ Conferences, 1200+ Symposiums and 1200+ Workshops on
Medical, Pharma, Engineering, Science, Technology and Business

Diethylaminoethyl Cellulose Immobilized Pointed Gourd (Trichosanthes dioica) Peroxidase in Decolorization of Synthetic Dyes

Farrukh Jamal1* and Tanvi Goel2
1Department of Biochemistry, Dr. Ram Manohar Lohia Avadh University, Faizabad-224001, U.P., India
2Division of Life Sciences, Research Centre, Nehru Gram Bharti University, Jhunsi, Allahabad-221505, U.P., India
Corresponding Author : Farrukh Jamal
Assistant Professor
Department of Biochemistry (DST-FIST & UGC-SAP Supported)
Dr. Ram Manohar Lohia Avadh University
Faizabad-224001, U.P., India
Fax: +91-05278-246330
E-mail: [email protected] or [email protected]
Received November 03, 2014; Accepted November 26, 2014; Published December 01, 2014
Citation: Jamal F, Goel T (2014) Diethyl Aminoethyl Cellulose Immobilized Pointed Gourd (Trichosanthes dioica) Peroxidase in Decolorization of Synthetic Dyes. J Bioprocess Biotech 4:187 doi: 10.4172/2155-9821.1000187
Copyright: © 2014 Jamal F, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

Visit for more related articles at Journal of Bioprocessing & Biotechniques


Diethylaminoethyl (DEAE) cellulose adsorbed Pointed Gourd Peroxidase (PGP) was employed in decolorization of synthetic dyes. The expressed activity of immobilized preparation on fifth repeated use was ~50% and decolorization achieved for synthetic dyes DR19 and dye mixture (DR19+DB9) was 64.9% and 61.5% respectively. Immobilized enzyme could effectively decolorize up to 88.2% and 77.4% of DR19 and dye mixture respectively in stirred batch process at 40°C whereas dye color removal monitored at 30°C and 50°C was comparatively low under similar conditions. Immobilized enzyme in the packed column used for the continuous removal of dye color could successfully decolorize DR19 and dye mixture to 69.4% and 51.4% after 50 d of operation. Thus, DEAE immobilized PGP is a simple, economical and effective preparation to remove color of synthetic dyes.

Pointed gourd peroxidase; Diethyl aminoethyl; Immobilization; Dye decolorization; Continuous reactor
The waste water from dye industries is rich in compounds that are toxic and detrimental to different life forms including humans. Color is usually the first contaminant to be recognized which affects the aesthetic merit, transparency and gas solubility of water bodies. The unused synthetic dyes in textile effluent mostly go untreated in the river and water bodies. Disperse dyes constitute the largest group of colorants used in the industry and are difficult to remove by chemical treatment. The processes involving physical and chemical treatment for decolorization of textile wastewater have numerous operational problems, and involve high cost [1]. On the other hand, most of the synthetic dyes are xenobiotic compounds which are poorly removed by the use of conventional biological aerobic treatments [2].
The dye color removal from wastewater is an area of technological innovations. In recent times, the approach has shifted towards enzyme based treatment of colored wastewater/industrial effluents. Enzymes are vital to new processes as they are environmental friendly and are capable of specifically reducing hazardous wastes. Peroxidases (EC are a group of heme-containing enzymes that have been isolated from diverse sources including plants, animals and microorganisms [3,4]. These enzymes have the ability to act on a number of aromatic compounds in the presence of hydrogen peroxide. The function of the latter is to oxidize the enzyme into its catalytically active form which in turn is capable of reacting with the phenolic contaminants [4]. However, during the reaction process these enzymes get inactivated and this inactivation might be due to the free radical formation during enzymatic reaction. These radicals are adsorbed on the enzymes active site thus, blocking the substrate binding sites [5].
Peroxidases are very useful in either removal of recalcitrant toxic compounds or transforming them into innocuous products. They can change the characteristics of a given waste rendering it more amenable for treatment [6]. Their catalytic action is extremely efficient and selective as opposed to chemical catalysts due to higher reaction rates, milder reaction conditions (relatively low temperature and in the entire aqueous phase pH range) and greater stereo specificity [7]. Though much attention has been paid in the utilization of biocatalysts in several fields, their involvement has been felt very recently in solving the environmental problems [8,9]. The use of free enzymes poses inherent limitations as the stability and catalytic ability of free enzymes decreases with the complexity of the effluents [10]. Some of these limitations are overcome by the use of enzymes in immobilized form which can be used as catalysts with long lifetime [10,11].
An extensive work has been done on the enzymatic removal of aromatic compounds from wastewater by using peroxidase and hydrogen peroxide [12]. Enzymatic method has some advantages over conventional methods of treatment which include: applicability over a broad range of pH, temperature, salinity and contaminant concentration, action on recalcitrant materials and simplicity in controlling the process [13]. However, an effective use of enzymes was hampered due to their non-reusability, sensitivity to various denaturants and high cost [14]. Some of these constraints may be overcome by immobilizing enzymes on various supports [15,16].
Work in the area of enzyme technology has provided significant clues that facilitate using enzymes optimally at large scale by cross-linking, entrapping and immobilizing [17,18]. The current study demonstrates a simple, inexpensive and high yield procedure for immobilization of Pointed Gourd Peroxidase (PGP) on DEAE cellulose for the dye color removal of disperses dyes. The decolorization of disperse dyes was done in batch process as well as in a continuous vertical bed-reactor. The reusability of the I-PGP for dye color removal was measured.
Materials and Methods
Bovine serum albumin, o-dianisidine HCl, Disperse Red 19 (DR19), Disperse Black 9 (DB9), DEAE cellulose, glutaraldehyde was procured from Sigma Chemical Co. (St. Louis, MO, USA). All other chemicals were of analytical grade. The pointed gourds were procured from local market.
Partial purification of PGP by ammonium sulphate precipitation
The protein was extracted from pointed gourd using ammonium sulphate as described previously [19]. This preparation of protein was aliquoted and stored for further use.
Protein estimation and assay of peroxidase (PGP) activity
Protein was estimated using the procedure of Lowry et al. [20]. The salt purified protein was assayed for peroxidase activity as describe by Jamal et al. [21,22]. Peroxidase activity was measured by the change in the optical density (λ=460 nm) at 37°C, by estimating the initial rate of oxidation of 6.0 mM o-dianisidine HCl in presence of 18.0 mM H2O2 in 0.1 M sodium acetate buffer (pH 5.6) for 15 min. Immobilized enzyme preparation was continuously agitated for entire duration of assay. One unit (1.0 U) of peroxidase activity was defined as the amount of enzyme protein that catalyzes the oxidation of 1mmol of o-dianisidine HCl in the presence of H2O2 per min at 37°C into colored product ( εm = 30 000 M-1 L-1)
Treatment and activation of DEAE cellulose
The activation of DEAE cellulose was done using method described elsewhere [17,23]. Briefly 6.0 g of DEAE cellulose was gently stirred and allowed to swell overnight in 150 mL of distilled water. The swollen DEAE cellulose was filtered with a Buchner Funnel and incubated with 120 mL of 0.5 N HCl for 1 h. Acid treated DEAE cellulose was collected by filtration on Buchner Funnel and was washed with distilled water continuously till it attained pH 7.0. 125 mL of 0.5 N NaOH was added to HCl treated DEAE cellulose and it was stirred on a magnetic stirrer for 1 h at 4°C. The treated ion exchanger was washed again with distilled water till it attained neutral pH. Further, it was suspended and stored in 100 mL of distilled water at 4°C.
Cross-linking of DEAE cellulose adsorbed PGP
PGP (1300 units) was added to 1.2 g of DEAE cellulose and stirred overnight at 4°C. The preparation was treated with 0.3% (v/v) glutaraldehyde for 2 h at 4°C with constant stirring. Cross-linking was performed in presence of o-dianisidine HCl. Ethanolamine was added to a final concentration of 0.01% (v/v) to stop cross-linking. The solution was allowed to stand for 90 min at room temperature and the pellet was collected by centrifugation at 3000 × g for 30 min on a cooling centrifuge 4°C [24,25].
Preparation of synthetic dye solutions and calculation of percent dye decolorization
The synthetic solutions of disperse dyes (30-50 mg/mL) were prepared in distilled water to examine their decolorization by soluble and immobilized PGP. A mixture of disperse dyes consisting of DR19 and DB9 was prepared by mixing each dye in equal proportion of color intensity [26]. To compare various experiments, the decolorization was calculated for each dye or mixture of dyes. Dye decolorization was monitored by measuring the difference at the maximum absorbance for each dye as compared with control experiments without enzyme on UV-visible spectrophotometer (JASCO V-550, Japan). Untreated dye solution (inclusive of all reagents except the enzymes) was used as control for calculation of percent decolorization. The dye decolorization was calculated as the ratio of the difference of absorbance of treated and untreated dye to that of treated dye and converted in terms of percentage. Three independent experiments were carried out in duplicate and the mean was calculated.
Reusability of immobilized PGP in the decolorization of disperse dye
DR19 and mixture of dyes (DR19+DB9) were incubated with immobilized PGP for 2 h as mentioned earlier. The enzyme was separated by centrifugation and stored in the assay buffer for over 12 h. Experiments was repeated upto 10 times with the same preparation of PGP and each time with a fresh batch of dye solution. Dye decolorization was monitored at specific wavelength maxima of the dye solutions. The percent decolorization was calculated by taking untreated dye or mixture of dyes as control (100%).
Decolorization of dye solution by soluble and immobilized peroxidase in batch processes
The dye solution (200 mL) was treated with soluble and immobilized PGP (180 U) in 100 mM sodium acetate buffer, pH 5.6 in the presence of 0.2 mM riboflavin as redox mediator and 0.8 mM H2O2 for different durations and at varying temperatures [21] . The treated samples were centrifuged at 3000 × g for 15 min. The residual dye concentration was measured spectrophotometrically at specific wavelength maxima of the dye. Untreated dye solution was considered as control (100%) for the calculation of percent decolorization.
Continuous dye decolorization using a vertical PGPimmobilized column
A packed bed-reactor system was developed for the continuous removal of dyes from solutions. A column (15 × 2.0 cm) was filled with DEAE cellulose immobilized PGP (1500 U) and equilibrated with 100 mM sodium acetate buffer pH 5.6. The flow rate was maintained at 12 mL h-1 and the feed solution contained either DR19 or mixture of DR19 and DB9 in two independent reactor systems. Dye solutions were run under the same experimental conditions. Reactors were operated at room temperature (37°C) for a period of 60 days. Treated samples were collected at an interval of 10 d and the absorbance of each sample was recorded.
Reusability and storage stability of DEAE-PGP complex in dye decolorization
Table 1 shows the expressed activity of DEAE-PGP complex. Immobilized PGP (I-PGP) expressed ~ 50% activities after being repeatedly use for five times. Thereafter, the expressed peroxidase activity declined progressively to 15.5% in the tenth use. I-PGP preparation was used to remove the dye color of disperse dye DR19 and dye mixture (DR19 and DB9). The decolorizing ability of I-PGP was 51.4% for DR19 in the eight repeated use whereas the dye mixture (DR19+DB9) showed 51.7% decolorization in the seventh repeated use. Thereafter, decolorizing potential of I-PGP underwent downfall progressively and was parallel to the decline in the expressed peroxidase activity of the I-PGP preparation.
Storage stability along with the potential to remove the dye color was monitored upto 60 d with an interval of 5 to 10 d. Table 2 shows the remaining activity in the stored preparations and their ability to remove the dye color. The 35 d stored I-PGP preparation expressed 53.4% peroxidase activity and decolorized DR19 and dye mixture (DR19+DB9) to 73.5% and 59.9% respectively. Thereafter the decolorization potential underwent downfall with the 60 d stored preparation expressing poor peroxidase activity (23.8%) and removed dye color to 29.3% (DR19) and 22.6% (DR19+DB 9).
Dye treatment in a stirred batch process at varying time and temperature
The decolorization of dyes by soluble and DEAE immobilized PGP was carried out at varying time durations and temperatures as shown in Table 3. It was observed that maximum dye color removal was achieved at 40°C with an exposure time of 2 h. Soluble PGP decolorized 80.9% and 74.1% of DR19 and mixture of dyes after 2 h of incubation, respectively. However, DEAE immobilized PGP was more effective and sustainable as compared to its soluble counterpart in the decolorization of both DR19 and mixture of dyes. Decolorization by I- PGP under similar conditions was 88.2% and 77.4% for DR19 and dye mixture respectively after 2 h of treatment. At lower temperature of 30°C, the performance of soluble PGP were lower with 76.9% and 55.1% dye color removal achieved after an incubation period of 2 h. However under similar conditions the I-PGP was much effective and decolorized DR19 and dye mixture to an extent of 78.4% and 65.4% respectively. Further, at 50°C and under similar conditions of incubation soluble PGP effectively removed the dye color of DR19 (55.9%) and dye mixture (51.2%). On increasing the incubation time (160 min), the dye color removal by soluble PGP was lowered to 31.3% (DR19) and 29.4% (DR19+DB9) whereas the performance of I-PGP was sufficiently higher 48.1% (DR19) and 60.2% (DR19+BB9). It was also observed that although, the optimum temperature was 40°C, yet I-PGP still retained sufficient potential at 50ºC as compared to that recorded at 30°C.
Dye decolorization in a packed vertical I- PGP column
Table 4 shows the dye color removal of DR19 and mixture of dyes (DR19+DB9) by passing through I-PGP packed vertical bed reactor. About 88.5% and 74.5% of dye decolorization was achieved even after 10 d of its continuous operation. With the increase in the duration of continuous operation there was decrease in the decolorization ability of the I-PGP packed column. On 30 d of continuous use I-PGP decolorized DR19 (77.4%) and dye mixture (69.5%). This decrease continued to 60 d with only 50.5% and 53.4% dye color recorded for DR19 and dye mixture respectively.
Immobilizing enzymes directly from crude homogenate is relatively a cost-effective and seemingly a feasible approach [27]. Although the immobilized form of bio-molecules holds commercial importance, protocols available for such preparations are limited. Immobilization by adsorption is an effective procedure for binding enzymes directly from partially purified preparations or even from crude homogenates [24]. The present study was aimed to immobilize PGP on a support which could be used to treat disperse dyes and dye mixtures which are generally present in textile effluents.
DEAE cellulose adsorbed PGP was cross-linked with glutaraldehyde and this preparation was found to be very efficient in removing the dye colors of disperse dyes viz., DR19 and dye mixture (DR19+DB9). I-PGP could be used seven times to achieve dye color removal of DR19 and dye mixture to over 50% which is considerably effective than soluble peroxidases. Immobilized preparation of enzymes has advantage over free enzyme as it could be reused several times and may also provide a better environment for the catalytic activity of enzyme [14,28]. Moreover, such enzymes in immobilized states can be stored for longer durations and relatively easier to handle and use. The data of storage stability of I-PGP suggest that immobilized preparations confer long lasting peroxidase activity which could be used in reactors for the treatment of effluents containing phenolic and other aromatic pollutants including dyes which are primarily represented in textile effluents. The reusability and storage experiments further supported that the use of such a cheaper source of enzyme and support will definitely minimize the cost of immobilization and provide a suitable approach for the treatment of huge volumes of wastewater in batch processes as well as in continuous reactors.
In our earlier studies we have shown that the dye color removal was poor when these dyes were treated without enzyme or only in the presence of redox mediator or the enzyme alone. Thus it’s essential that the enzyme catalytic activity is effective in conjunction with redox mediators and optimum concentration of hydrogen peroxide [4,19]. Further, the enzyme works well in acidic pH (usually in the range of 3 to 6) and therefore the study was performed at pH 5.6 (data not shown). The decolorization data indicates that the enzyme retained sufficient activity in the immobilized state at the operational pH.
The dyes tested may have a narrow redox potential range and perhaps a correlation exists between redox potential and dye reduction rates. It is known that the closer the redox potential is between dye and redox mediator, the faster is dye reduction, because electron transfer is facilitated due to the low potential difference. Such behavior explains the better catalytic properties of riboflavin. However, dye reduction rate is not only determined by redox potential, but also by other factors such as chemical structure, environmental conditions and anaerobic sludge affinity and concentration. The chromophore cleavage by PGP in conjunction with redox mediators was favorable for azo dyes, because the reduction occurs in the nitrogen bonds, which have more affinity to receive electrons, based on electronegative properties, as compared to carbon-carbon bond chromophore of the anthraquinone dyes. Therefore, the effect of redox mediators on dye reduction is related to the molecular structure, being more evident for azo dyes with low decolorization rates in the absence of these compounds, and ineffective for anthraquinone dyes because of the structural stability of the latter [26].
Our studies showed that immobilized peroxidase was much more effective in removing dye color as compared to soluble enzyme in a batch process. It may be due to the reason that immobilization shielded the number of reactive free amino groups, which are not protected in soluble case and hence, were more susceptible to reaction with the reactive products like free radicals [29]. Our findings are in accordance to our earlier studies using immobilized PGP-Concanavalin A complex on calcium alginate pectin gel in decolorization of synthetic dyes [24].
To evaluate the efficiency of immobilized PGP on a large scale for the removal of dye color, a vertical continuous reactor system was designed and operated continuously with a flow rate of 15 mL h-1. In this work, a flow rate of 15 mL h-1 was maintained to run the reactor without any operational problem like clogging which may be of concern since precipitate is formed during the enzymatic reaction. Both the reactors worked for more than 60 d approximately, thus explaining their efficiency towards dye decolorization. A significant loss of color appeared when DR19 or mixture of dyes was treated with I- PGP in the presence of redox mediator, riboflavin in a continuous reactor system. It has earlier been reported that the disappearance of peak in visible region was either due to the breakdown of chromophoric groups present in dyes or the removal of pollutants in the form of insoluble products [23].
One of the remarkable properties of the immobilized enzyme over its soluble counterpart was that it can be separated from the reaction mixture and hence, can be reused repeatedly to transform its substrate. Although PGP immobilized on DEAE cellulose was losing its activity over repeated uses, the decrease in efficiency of the enzyme after few cycles may be due to the binding of the active sites of the enzyme by the product produced during the enzymatic reactions [30].
The preparation and application of DEAE-immobilized pointed gourd peroxidase in decolorization of synthetic dyes was investigated. The data of the present work reveals the effectiveness of the immobilized peroxidase in sustainable dye color removal. The DEAE immobilized PGP expressed remarkable peroxidase activity, can be repeatedly used and stably stored for long periods. The system in this study is developed with a cheaper biocatalyst that is quite effective in treating dyes continuously in a small laboratory reactor. The enzymes in soluble form cannot be exploited on large scale due to their limitations of stability and reusability. Consequently, the use of immobilized enzymes has significant advantages over soluble enzymes. In the near future, cost effective, eco-friendly technologies based on the enzymatic approach for treatment of dyes present in the industrial effluents/wastewater will play a vital role. By immobilization using adsorption on DEAE, the apparent rate of enzyme inactivation was reduced which allowed a significant reduction in enzyme requirements for treatment. This increases enzyme lifetime which represents a very significant saving in terms of treatment costs.
We are thankful to the Department of Science and Technology (DST-FIST) under the Ministry of Science and Technology for providing financial assistance towards infrastructure development for carrying out this work. There is no conflict of interest whatsoever regarding this manuscript.

Tables and Figures at a glance


Table icon Table icon Table icon Table icon
Table 1 Table 2 Table 3 Table 4
Select your language of interest to view the total content in your interested language
Post your comment

Share This Article

Relevant Topics

Recommended Conferences

  • International Conference on Nanobiotechnology
    July 10-11, 2017 CHICAGO, USA
  • Global Biotechnology Congress 2017
    July 10th - 13th, 2017, Boston, MA, USA
  • 17th Euro Biotechnology Congress
    September 25-27, 2017 Berlin, Germany
  • 2nd World Biotechnology Congress
    December 04-06, 2017 Sao Paulo, Brazil

Article Usage

  • Total views: 11511
  • [From(publication date):
    December-2014 - Jun 29, 2017]
  • Breakdown by view type
  • HTML page views : 7755
  • PDF downloads :3756

Post your comment

captcha   Reload  Can't read the image? click here to refresh

Peer Reviewed Journals
Make the best use of Scientific Research and information from our 700 + peer reviewed, Open Access Journals
International Conferences 2017-18
Meet Inspiring Speakers and Experts at our 3000+ Global Annual Meetings

Contact Us

© 2008-2017 OMICS International - Open Access Publisher. Best viewed in Mozilla Firefox | Google Chrome | Above IE 7.0 version